25.04.2013 Views

Vegetation Classification and Mapping Project Report - USGS

Vegetation Classification and Mapping Project Report - USGS

Vegetation Classification and Mapping Project Report - USGS

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

<strong>USGS</strong>-NPS <strong>Vegetation</strong> <strong>Mapping</strong> Program<br />

Colonial National Historical Park<br />

<strong>Vegetation</strong> Map Production<br />

The final map for Colonial National Historical Park depicts 40 map classes. Twenty-six map<br />

classes are crosswalked to USNVC vegetation associations, seven are nonst<strong>and</strong>ard, park-specific<br />

vegetation classes, <strong>and</strong> seven are Anderson l<strong>and</strong>-use classes. Because of the difficulty of<br />

distinguishing certain associations on aerial photography, two map classes, Tidal Oligohaline<br />

Marsh <strong>and</strong> Tidal Mesohaline <strong>and</strong> Polyhaline Marsh, represent more than one USNVC<br />

association. Polygons mapped as Tidal Mesohaline <strong>and</strong> Polyhaline Marsh represent vegetation<br />

belonging to one or two associations. Polygons mapped as Tidal Oligohaline Marsh represent<br />

one to five associations, occurring singly or as a complex. Polygons representing multiple<br />

associations were not labeled to the association level. Each polygon representing a single<br />

USNVC association was attributed with the appropriate USNVC formation <strong>and</strong> alliance based on<br />

the hierarchy of the USNVC. Polygons mapped as nonst<strong>and</strong>ard classes were also attributed to<br />

USNVC formations when possible. The final map table includes 14 formations, 33 alliances,<br />

<strong>and</strong> 24 associations.<br />

The Kappa index for the final vegetation map exceeds the <strong>USGS</strong>-NPS VMP protocol<br />

requirement of 80%. Errors of commission <strong>and</strong> omission reported for seven map classes fall<br />

below the <strong>USGS</strong>-NPS VMP protocol requirement of 80%. Examination of the errors associated<br />

with each observation shows they can be attributed to below minimum mapping unit inclusions<br />

of other vegetation types within the target polygons, to the incomplete survey of target polygons,<br />

to seasonal constraints in identifying certain associations in the field, or to observations made in<br />

ecotonal areas transitional to other vegetation types. Additionally, some of the mapping errors<br />

were due to the difficulty of distinguishing deciduous associations on aerial photography, since<br />

many deciduous signatures are virtually identical.<br />

Aerial photography flown in March 2002 served as the base map for the final vegetation map.<br />

Since that time, the vegetation in the park has continued to change. In September 2003,<br />

Hurricane Isabel altered the mapped vegetation in many areas of the park. The temporal<br />

progression of transitional vegetation <strong>and</strong> the natural dynamics of coastal areas will continue to<br />

alter the mapped vegetation, as will the park’s ongoing management of invasive species. Despite<br />

these changes, the vegetation map produced by this project provides crucial baseline data for the<br />

park resource managers.<br />

Recommendations for Future <strong>Project</strong>s<br />

Invasive nonnative plant species are the main threat to the native vegetation associations at<br />

Colonial National Historical Park. Continued monitoring <strong>and</strong> management of invasive species in<br />

<strong>and</strong> around all the natural communities in the park should be a priority for the park’s resource<br />

managers. Early detection <strong>and</strong> control of invasive nonnative species on forest edges <strong>and</strong> along<br />

trails <strong>and</strong> roads can help prevent new invasions. The most common <strong>and</strong> problematic species<br />

include Japanese honeysuckle, Nepalese browntop, <strong>and</strong> common reed. Dormant season herbicide<br />

application can be effective in treating Japanese honeysuckle infestations, but timing is critical. As<br />

a rule, foliar application of 1.5% glyphosate (e.g., Roundup) after the first killing frost <strong>and</strong> before<br />

the first hard frost is most effective (Nuzzo 1997). The annual, Nepalese browntop is a prolific<br />

seed-producer, <strong>and</strong> seed banks can persist for at least five years (Tu 2000). Control of the<br />

species can be very labor intensive (i.e., h<strong>and</strong>-pulling) or destructive to non-target plants (i.e.,<br />

83

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!